International Journal of Aquatic Biology (2014) 2(6): 330-336 

ISSN: 2322-5270; P-ISSN: 2383-0956

Journal homepage: www.NPAJournals.com 
© 2013 NPAJournals. All rights reserved 

Original Article 

Morphological variation of shad fish Alosa brashnicowi (Teleostei, Clupeidae) populations 
along the southern Caspian Sea coasts, using a truss system 

 
Sara Paknejad1, Adeleh Heidari2, Hamed Mousavi-Sabet*21 

 
1Department of Fisheries, Islamic Azad University, Tonekabon Branch, Mazandaran, Iran. 

2Department of Fisheries, Faculty of Natural Resources, University of Guilan, Sowmeh Sara, P.O. Box: 1144, Guilan, Iran. 

 
Article history: 
Received 1 July 2014 

Accepted 5 October 2014 

Available online 2 5 December 2014 

 
Keywords:  
Caspian Sea  

Alosa braschnicowi  
Truss system  

Shad fish 

Morphometrics 

Abstract: A 15-landmark morphometric truss network system was used to investigate the hypothesis 
of population fragmentation of Shad fish Alosa braschnicowi Borodin, 1904 along the southern 

Caspian Sea. A total of 181 A. braschnicowi specimens were caught from six localities, respectively 

from the west to the east including; Astara, Rezvanshahr, Anzali, Tonekabon, Sari and Miankale. 

Principal component analysis, canonical variates analysis and clustering analysis were used to 

examine morphological differences. Univariate analysis of variance showed significant differences 

between the means of the six groups for 72 standardized morphometric measurements out of 105 

characters studied. In canonical variates analysis, the overall assignment of individuals into their 

original groups was 71.46% and scatter plot of individual component scores between CV1 and CV2 

showed fish specimens grouped into six areas. Clustering analysis based on Euclidean square distances 

among groups of centroids using UPGMA resulted into six main clusters indicating morphologically 

distinction populations of A. braschnicowi in the region. These populations of A. braschnicowi are 

distinguished especially by head shape, eye diameter, and pre-dorsal, pre-pelvic and pre-anal 

distances. Therefore, it is suggested considering these morphologically different populations as 

distinct stock in the southern Caspian Sea coasts. 
 

Introduction 

The study of morphological characters with the aim 

of defining or characterizing fish stock units, has a 

great interest in ichthyology (Bektas and Belduz, 

2009). The morphometric characters is particularly 

important where the differences are mostly attributed 

to environmental influences rather than genetic 

differentiation (Bektas and Belduz, 2009). 

Geographical isolation of populations and 

interbreeding can lead to morphometric variations 

between populations, and this morphometric 

variation can provide a basis for population 

differentiation (Bookstein, 1991). 

The family Clupeidae is found in warmer marine 

waters with some anadromous or permanent 

freshwater residents. This family has about 200 

                                                           
* Corresponding author: Hamed Mousavi-Sabet 

E-mail address: mousavi-sabet@guilan.ac.ir 

species in 56 genera worldwide (Eschmeyer and 

Fong, 2011; Coad, 2014), with eight reported species 

in the Caspian Sea. Alosa braschnicowi is an 
economically important clupeids of the Caspian Sea 

that widely distributed across this sea. This species 

distributes in the south in winter, moving north to 

spawn in spring (Coad, 2014). The morphometric 

characters between male and female sexes in this 

species did not different (Whitehead, 1985). The 

study of morphometrics using the truss network 

system is effective in capturing information about 

the shape of an organism (Kocovsky et al., 2009). It 

covers the entire fish in a uniform network, and 

theoretically, increases the likelihood of extracting 

morphometric differences between specimens 

(Kocovsky et al., 2009; Cakmak and Alp, 2010). 



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Paknejad et al/ Morphological variation of A. brashnicowi along the southern Caspian Sea coasts 

Therefore, it has been used in the differentiation of 

various populations within a species and also various 

species (Kocovsky et al., 2009). Various effects of 

the geographical isolation on fish population in the 

southern Caspian Sea basin have been documented 

in the recent past (Mousavi-Sabet et al., 2011; 

Mousavi-Sabet et al., 2012; Mousavi-Sabet and 

Anvarifar, 2013; Kohestan-Eskandari et al., 2014). 

However, the variability of the A. braschnicowi 
population parameters and its spatial distribution has 

not been studied in Iranian waters of the Caspian 

Sea. Therefore, propose of this study was to use a set 

of morphometric characters for examine whether 

specific ecological constraints, due to geographic 

variation, could affect the formation of stock 

separation for this species.  

 

Materials and methods 

A total of 181 specimens of A. braschnicowi were 
randomly collected by beach seine from six fishing 

regions along the southern Caspian Sea coasts, 

including the Miankale (36°54′10.89″ N, 

53°48′48.33″ E; 31 individuals), Sari (36°48′04.63″ 

N, 53°02′07.50″ E; 30 individuals), Tonekabon 

(36°50′20.97″N, 50°50′17.25″E; 30 individuals), 

Anzali (37°29′29.86″ N, 49°27′39.59″ E; 30 

individuals), Rezvanshahr (37°36′32.19″ N, 

49°08′25.54″ E; 30 individuals) and Astara 

(38°23′47.40″ N, 48°54′10.17″ E; 30 individuals) in 

November 2011 (Fig. 1). The sampled fish were 

fixed in 10% formaldehyde at the sampling sites and 

transported to the laboratory. 

For extracting morphometric data, the left side of 

fishes were photographed by a 300-dpi, 32-bit color 

digital camera (Cybershot DSC-F505; Sony, Japan) 

with dorsal and anal fins erected by pins. A total of 

105 distance measurements between 15 landmarks 

were surveyed using the truss network system 

according to Bookstein (1991) with minor 

modifications (Fig. 2). Images were saved in jpg 

format, and the defined landmark points were 

digitized using TpsDig2 (Mustafic et al., 2008) on 

pictures. A box truss of 26 lines connecting the 

landmark points was generated for each fish to 

represent the basic shape of fish (Bookstein, 1991; 

Mustafic et al., 2008). All measurements 

transformed into linear distances for subsequent 

analysis (Mustafic et al., 2008). An allometric 

method was used to remove size-dependent variation 

in morphometric characters using following 

formula: Madj = M (Ls / L0)b, where M is the original 
measurement, Madj the size adjusted measurement, 

L0 the standard length of the fish, Ls the overall mean 
of the standard length for all fish from all samples in 

each analysis, and b was estimated for each character 
from the observed data as the slope of the regression 

of log M on log L0 using all fish in any group. The 
results derived from the allometric method were 

confirmed by testing significance of the correlation 

between transformed variables and standard length 

(Mustafic et al., 2008).  

The sex of specimens was determined 

macroscopically, and there were no significant 

differences in tested variables between the sexes 

within the same stock. Therefore, the data for both 

Figure 1. Sampling site locations of A. braschnicowi along the 
southern Caspian Sea coast. 

Figure 2. Locations of the 15 landmarks for constructing the truss 

network on A. braschnicowi. 1- tip of snout; 2- anterior edge of 
eye; 3- posterior edge of eye; 4- posterior tip of maxillary; 5- 

forehead (end of frontal bone); 6- end of operculum; 7- dorsal 

origin of pectoral fin; 8- origin of dorsal fin; 9- origin of pelvic 

fin; 10- termination of dorsal fin; 11- origin of anal fin; 12- 

termination of anal fin; 13- dorsal side of caudal peduncle, at the 

nadir; 14- ventral side of caudal peduncle, at the nadir; 15- end of 

body lateral line. 



332 
 

International Journal of Aquatic Biology (2014) 2(6): 330-336 

sexes were pooled for all subsequent analyses.  

Univariate analysis of variance (ANOVA) was 

performed for each morphometric character to 

evaluate the significant difference between the six 

populations (Rodriguez et al., 2010). Those 

morphometric characters which showed highly 

significant variations (P≤0.01) were used to achieve 

the recommended ratio of the number of organisms 

measured (N) to the parameters included (P) in the 

analysis of at least 3–3.5 (Bookstein, 1991) to obtain 

a stable outcome from multivariate analysis. The 

principal component analysis (PCA), canonical 

variates analysis (CVA) and cluster analysis (CA) by 

adopting the Euclidean square distance as a measure 

of dissimilarity and UPGMA (Unweighted Pair 

Group Method with Arithmetical average) as the 

clustering algorithm (Yakubu et al., 2011) were 

employed to discriminate the six populations. 

Statistical analyses for morphometric data were 

performed using the SPSS version 16 software 

package. 

To determine the most effective morphometric 

Characters F P Characters F P Characters F P Characters F P 

1-2 0.000 1.000 3-4 2.801 0.019 5-9 7.800 0.000 8-11 3.636 0.004 

1-3 25.690 0.000 3-5 6.842 0.000 5-10 3.547 0.005 8-12 6.034 0.000 

1-4 11.691 0.000 3-6 2.720 0.022 5-11 4.875 0.000 8-13 1.980 0.085 

1-5 6.637 0.000 3-7 1.169 0.327 5-12 3.665 0.004 8-14 5.013 0.000 

1-6 13.629 0.000 3-8 7.566 0.000 5-13 5.467 0.000 8-15 4.246 0.001 

1-7 12.917 0.000 3-9 3.790 0.003 5-14 2.905 0.015 9-10 0.517 0.763 

1-8 7.118 0.000 3-10 5.837 0.000 5-15 3.658 0.004 9-11 4.800 0.000 

1-9 3.654 0.004 3-11 3.430 0.006 6-7 9.633 0.000 9-12 1.729 0.131 

1-10 1.298 0.267 3-12 5.928 0.000 6-8 7.476 0.000 9-13 1.807 0.114 

1-11 5.886 0.000 3-13 3.609 0.004 6-9 3.316 0.007 9-14 2.028 0.078 

1-12 3.354 0.007 3-14 4.244 0.001 6-10 8.110 0.000 9-15 1.606 0.161 

1-13 5.519 0.000 3-15 7.471 0.000 6-11 3.348 0.007 10-11 1.960 0.088 

1-14 6.359 0.000 4-5 9.823 0.000 6-12 6.974 0.000 10-12 1.401 0.227 

2-3 28.648 0.000 4-6 3.275 0.008 6-13 5.541 0.000 10-13 0.443 0.818 

2-4 9.007 0.000 4-7 0.086 0.994 6-14 4.937 0.000 10-14 0.822 0.536 

2-5 7.263 0.000 4-8 3.720 0.003 6-15 9.226 0.000 10-15 0.425 0.831 

2-6 14.608 0.000 4-9 2.135 0.064 7-8 2.386 0.041 11-12 2.907 0.015 

2-7 14.325 0.000 4-10 2.523 0.032 7-9 5.660 0.000 11-13 3.253 0.008 

2-8 7.073 0.000 4-11 1.837 0.109 7-10 3.010 0.012 11-14 1.164 0.330 

2-9 2.917 0.000 4-12 2.746 0.021 7-11 2.020 0.079 11-15 1.951 0.089 

2-10 1.472 0.202 4-13 1.659 0.148 7-12 4.070 0.002 12-13 1.746 0.127 

2-11 5.020 0.000 4-14 1.945 0.090 7-13 2.921 0.015 12-14 0.410 0.842 

2-12 1.167 0.328 4-15 3.272 0.008 7-14 2.026 0.078 12-15 2.963 0.014 

2-13 2.895 0.016 5-6 12.284 0.000 7-15 4.412 0.001 13-14 0.837 0.525 

2-14 4.422 0.001 5-7 18.966 0.000 8-9 1.209 0.307 13-15 0.389 0.856 

2-15 2.595 0.028 5-8 8.181 0.000 8-10 3.924 0.002 14-15 0.998 0.421 

 

Table 1. The results of ANOVA for morphometric measurements of A. braschnicowi populations along the southern Caspian Sea. 

 



333 
 

Paknejad et al/ Morphological variation of A. brashnicowi along the southern Caspian Sea coasts 

measurement to differentiate studied populations, 

the contributions of variables to principal 

components (PC) were examined. To examine the 

suitability of the data for PCA, Bartlett’s Test of 

sphericity and the Kaiser–Meyer–Olkin (KMO) 

measures were performed. The Bartlett’s Test of 

sphericity, tests the hypothesis that the values of the 

correlation matrix equal zero and the KMO measure 

of sampling adequacy tests, whether the partial 

correlation among variables is sufficiently high 

(Yakubu et al., 2011). The KMO statistics vary 

between 0 and 1 and the values greater than 0.5 are 

acceptable (Nimalathasan, 2009; Yakubu et al., 

2011).  

 

Results 

The correlation between transformed morphometric 

variables and standard length was not significant 

(P>0.05) which confirms that size or allometric 

signature on the basic morphological data was 

accounted. Significant differences between six 

populations of A. braschnicowi were observed in 
terms of 72 morphometric characters out of 105 

studied (Table 1). Of these 72 characters, 60 

characters were found to be highly significant 

(P≤0.01) and were used for further multivariate 

analysis. In this study N:P ratio was 3.01 (181/60) 

that revealed samples size were adequate. 

The value of KMO for overall matrix is 0.695, and 

the Bartlett’s Test of sphericity is significant 

(P≤0.01). The results of KMO and Bartlett’s suggest 

that the sampled data is appropriate to proceed with 

a factor analysis procedure. 

Principal component analysis of 60 morphometric 

measurements extracted 12 factors with Eigen 

values>1, explaining 94.52% of the variance (Table 

2). The first principal component (PC1) accounted 

for 25.94% of the variation and the second principal 

component (PC2) for 15.33% (Table 2), and the most 

significant loadings on PC1 were 1-3, 1-4, 1-6, 1-7, 

1-9, 1-11, 1-12, 1-13, 1-14, 2-3, 2-6, 2-7, 2-11, 3-13, 

3-14, 3-15, 4-6, 5-6, 5-7, 5-9, 6-8, 6-10, 6-11, 6-12, 

6-13 6-14, 6-15, 7-15 and on PC2 were 1-8, 2-8, 3-

8, 4-8, 5-8, 6-8, 8-10, 8-11, 8-12, 8-14, 8-15. In this 

analysis, the characteristics with an Eigen value 

exceeding 1 were included, and others discarded. 

The CV1 and CV2 were plotted to allow visual 

examination of the distribution of each locality 

sample along the CVs (Fig. 3). In the scatter plot, the 

Miankale, Astara and Anzali specimens were 

grouped together in the same quadrant with high 

value for CV1 and low value for CV2 (quadrate IV), 

Tonekabon in a quadrant with low value for both 

CVs (quadrate III), Rezvanshahr in a quadrant with 

Factor Eigenvalues 
Percentage of 

variance 

Percentage of 

cumulative variance 

1 15.567 25.945 25.945 

2 9.203 15.338 41.283 

3 7.332 12.220 53.503 

4 6.235 10.392 63.895 

5 3.961 6.601 70.496 

6 3.198 5.330 75.826 

7 2.662 4.437 80.263 

8 2.609 4.348 84.611 

9 1.907 3.179 87.789 

10 1.771 2.952 90.741 

11 1.178 1.963 92.704 

12 1.094 1.823 94.527 

 

Table 2. Eigen values, percentage of variance and percentage of cumulative variance of principal component analysis of morphometric 

measurements for A. braschnicowi populations along the southern Caspian Sea. 



334 
 

International Journal of Aquatic Biology (2014) 2(6): 330-336 

high value for both CVs (quadrate II) and finally Sari 

in a quadrant with low value for CV1 and high value 

for CV2 (quadrate I). The overall random 

assignment of individuals into their original groups 

was high (71.46%), indicating that these samples are 

probably divergent from each other (Fig. 3).  

The dendrogram derived from CA of Euclidean 

square distances among groups of centroids showed 

six main clusters based on morphometric 

characteristics. Despite the geographical distance 

between the Miankale and Sari regions and 

Rezvanshahr and Anzali regions, morphometric 

clustering revealed that the individuals of these 

locations form the same clade with great 

homogeneity, while Tonekabon and Astara exhibited 

higher heterogeneity, confirming the results obtained 

from discriminant analysis for this species (Fig. 4). 

 

Discussion 

The multivariate analysis of morphometric 

characteristics classified the A. braschnicowi 
populations along the southern Caspian Sea coasts 

into six distinct groups. The results demonstrate that 

there are morphologically distinct populations of 

Figure 3. Scatterplot of group centroids of standardized canonical variates functions 1 (CV1) and 2 (CV2) for morphometric characteristics of six 

populations of A. braschnicowi along the southern Caspian Sea. 

Figure 4. Dendrogram derived from cluster analyses of morphometric measurements on the basis of Euclidean distance for A. braschnicowi 
populations along the southern Caspian Sea. 



335 
 

Paknejad et al/ Morphological variation of A. brashnicowi along the southern Caspian Sea coasts 

A. braschnicowi particularly for Tonekabon region. 
These morphological differences is solely related to 

body shape variation and not to size effects which 

were successfully accounted by allometric 

transformation. Size-related traits play a 

predominant role in morphometric analysis and the 

results may be erroneous if not removed from data 

(Bookstein, 1991; Buj et al., 2008; Torres et al., 

2010).  

The analysis of variance also revealed significant 

phenotypic variation among the six populations. 

CVA could be a useful method to distinguish 

different stocks of the same species (Yakubu and 

Okunsebor, 2011). The present study showed a high 

differentiation among the populations of 

A. braschnicowi in the studied areas. This 
segregation was partly confirmed by PCA, where 

revealed that the populations were distinct from each 

other.  

The causes of morphological differences among 

populations are often quite difficult to explain 

(Bookstein, 1991). It has been suggested that the 

morphological characteristics of fishes are 

determined by genetic, environment and the 

interaction between them (Heidari et al., 2013; 

Kohestan-Eskandari et al., 2014). The environmental 

factors prevailing during the early development 

stages, when the individual’s phenotype is more 

amenable to environmental influence is of particular 

importance (Eschmeyer and Fong, 2011). The 

phenotypic variability may not necessarily reflect 

population differentiation at the molecular level 

(Bookstein, 1991). Apparently, different 

environmental conditions can lead to an 

enhancement of pre-existing genetic differences, 

providing a high interpopulation structuring 

(Eschmeyer and Fong, 2011; Heidari et al., 2013; 

Mousavi-Sabet and Anvarifar, 2013).  

The Tonekabon (in the south-central part of the 

Caspian Sea), Miankale (in the southeast part of the 

sea) and Astara (in the southwest part of the sea) 

specimens are more distinct from the others. The 

distinctive environmental conditions of the 

Tonekabon, Miankale and Astara relative to the 

other studied areas may underlie the morphological 

differentiation among these three populations. The 

studied populations are distinguished from each 

other by morphologic differences especially in head 

shape, eye diameter, and pre-dorsal, pre-pelvic and 

pre-anal distances.   

Geographical isolation can also affect growth pattern 

and reproductive strategy of fish species. The 

importance of such factors on producing 

morphological differentiation in fish species is well-

known (Yamamoto et al., 2006; Pollar et al., 2007; 

Heidari et al., 2013). 

As conclusion, the present study proposes high 

morphological differentiation among 

A. braschnicowi populations along the southern 
Caspian Sea coasts. The results also suggest these 

morphologically different populations should be 

considered as distinct stock in the southern Caspian 

Sea in fisheries management and commercial 

exploitation of this species and any stock 

enhancement program. Nevertheless, future studies 

on determination of population structure will be 

elucidated using biochemical and molecular genetics 

methods. 

  

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